Field observations and models have shown: (1) differences in dispersal
and dormancy strategies could account for species coexistence in dist
urbed environments, (2) small scale disturbances contribute to species
coexistence in plant communities, and (3) recolonization success may
depend on the spatial pattern of suitable sites for establishment. A s
patially explicit, two-species, simulation model was developed to exam
ine the interaction between dispersal strategies, dormancy strategies
and small-scale disturbances on the pattern of coexistence of two annu
al plant species in patchy landscapes. Patchy landscapes with three hi
erarchical levers of structure were randomly generated and the dynamic
s for species differing in mean dispersal distance and dormancy strate
gy was simulated. The results showed that when species differed only i
n mean dispersal distance, the species with the shorter range dispersa
l would always displace the other. When disturbances prevented reprodu
ction and activated dormant seeds, then differences in dormancy strate
gy could result in coexistence of species with different dispersal cap
abilities. When species differed only in their dormancy fate (i.e., th
e proportion of dormant seeds produced per year), the range of disturb
ance intensities allowing coexistence was rather narrow: but differenc
es in the response of species to disturbance (i.e., disturbance-broken
seed dormancy versus gradual germination of dormant seeds) allowed co
existence under a wider range of disturbance intensities. These result
s suggest that differences in the ways species exploit the resources i
n space and time can mediate coexistence through storage effects. The
patterns of coexistence obtained in the simulations were consistent wi
th conclusions of a field study, in species-rich Mediterranean old-fie
lds, about the role for coexistence of the interactions among dispersa
l and dormancy strategies, spatial heterogeneity, and small-scale dist
urbances. Coexistence patterns depended on the degree of suitability a
nd the patchiness of the landscapes, mostly in relation to the interac
tions between landscape structure and mean dispersal distance, but als
o through complex interactions with dormancy characteristics. Therefor
e, disturbance regimes are not sufficient for predicting patterns of c
oexistence, and the unique spatial features of the landscapes need to
be taken into account.